A Dual-Functional Electroactive Filter Towards Simultaneously Sb(III) Oxidation and Sequestration
Özet
A protocol for the rational design of a dual-functional electroactive filter consisting of carbon nanotubes and titanate nanowires is reported and their environmental applications towards Sb(III) oxidation and sequestration is presented.
Abstract
We have designed a facile method to synthesize a dual-functional electrochemical filter consisting of two 1-D materials: titanate nanowires and carbon nanotubes. The hybrid titanate-CNT filter was prepared by a sonication coupled with a post-filtration route. Due to the synergistic effects of the increased number of exposed sorption sites, electrochemical reactivity, small pore size of the titanate-CNT network coupled with a flow-through design, simultaneous Sb(III) oxidation and sequestration can be readily achieved. Atomic fluorescence spectrometer technology demonstrated that the applied electrical field accelerates the Sb(III) conversion rate and the as-obtained Sb(V) were adsorbed effectively by the titanate nanowires due to their Sb specificity. This protocol provides a practical solution for the removal of highly toxic Sb(III) and other similar heavy metal ions.
Introduction
Recently, the environmental pollution caused by emerging antimony (Sb) has attracted much attention1,2. Extensive studies demonstrate that Sb compounds pose high toxicity to human and microorganisms, although present in low concentrations in the environment3,4. Even worse, conventional physicochemical or biological methods are usually ineffective to remove these emerging contaminants due to their low concentrations and high toxicity5. The most abundant species of Sb are Sb(V) and Sb(III), of which the latter form is more toxic.
Among the currently available treatment methods, adsorption is believed to be a promising and feasible alternative due to its high efficiency, low cost, and simplicity6,7. Till now, several nanoscale sorbents with tunable microstructures, large specific surface area and Sb specificity have been developed, such as TiO28, MnO29, titanate10, zerovalent iron11, iron oxides and other binary metal oxides12,13. A common problem when dealing with nanoscale adsorbents is the post-separation issue due to their small particle size. One strategy to address this issue is to load these nano-sorbents onto macro/micro-scale supports14. Another challenging issue restricting the wide application of adsorption technology is the poor mass transport caused by limited concentration of target compounds/molecules15. This issue may be partially addressed by adopting a membrane design and convention could enhance the mass transport significantly. Recent efforts have been devoted to develop advanced treatment systems that combine adsorption and oxidation in a single unit for effective Sb(III) removal. Here, we show how an electroactive titanate-carbon nanotube (titanate-CNT) filter was rationally designed and applied for the simultaneously adsorption and sequestration of toxic Sb(III). By fine-tuning the titanate loading amount, applied voltage, and flow rate, we demonstrate how the Sb(III) oxidation rate and sequestration efficiency can be tailored correspondingly. Although the fabrication and application of the electroactive filter is shown in this protocol, similar designs can also apply to the treatment of other heavy metal ions.
Minor changes in the fabrication process and reagents may cause significant changes in the morphology and performance of the final system. For instance, the hydrothermal time, temperature, and chemical purity have been shown to affect the microstructures of these nanoscale adsorbents. The flow rate of the adsorbate solution also determines the residence time within a flow-through system as well as the removal efficiency of target compounds. With clear identification of these key impacting parameters, a reproducible synthesis protocol can be secured and a stable removal efficiency of Sb(III) can be achieved. This protocol aims to provide detailed experience on the fabrication of dual-functional hybrid filters as well as their applications towards the removal of toxic heavy metal ions in a flow-through manner.
Protocol
CAUTION: Please carefully read relevant safety data sheets (SDS) of all chemicals and wear proper personal protection equipment (PPE) before use. Some of the chemicals are toxic and irritant. Be careful when handling carbon nanotubes, which may have additional hazards if inhaled or contacted by skin.
1. Preparation of the electroactive titanate-CNT filter
- Preparation of titanate nanowires16
- Dissolve 56 g of potassium hydroxide (KOH) in 100 mL of deionized water under vigorous stirring.
- Add 3 g of titanium dioxide (TiO2) powder into the as-dissolved KOH solution.
- Transfer the above solution into a Teflon-lined reactor and keep it at 200 °C for 24 h.
- Wash the obtained white precipitate with 0.1 mol/L hydrochloric acid (HCl) and deionized water until a neutral effluent pH is obtained. Dry the product under vacuum at 60 °C overnight.
- Transfer the products to a tube furnace and heat it to 600 °C for 2 h with a ramp rate of 1 °C/min.
- Preparation of titanate-CNT filter17
- Add 20 mg of carbon nanotubes (CNTs) into 40 mL of n-methyl pyrrolidone (NMP). Probe-sonication for 40 min to obtain homogeneous solution.
- Separately, add 20 mg of the as made titanate nanowires into 20 mL of NMP. Perform probe-sonication for 20 min.
- Mix the titanate dispersion solution with the CNT dispersion solution. Filter the mixture solution onto a PTFE membrane, which serves as a support for the titanate-CNT filter.
- Rinse sequentially with 100 mL of ethanol and 200 mL of deionized water.
NOTE: A CNT-alone filter can be prepared by a similar route without the addition of titanate nanowires.
2. Electrochemical filtration of Sb(III)
- Description on the experimental apparatus18
- Conduct the sorption experiments in an electrochemistry modified polycarbonate filtration casing (see Figure 1).
- Use a DC power supply to drive the electrochemistry.
- Adopt perforated titanium ring as connector for anodic or cathodic filters.
- Use an insulating silicone rubber as a separator and seal.
- Filtration experiments
- Add 2.2 mg of C8H4K2O12Sb2.3H2O into 1000 mL of deionized water to prepare 800 μg/L Sb(III) solution.
- Transfer 100 mL of Sb(III) solution to a 150 mL beaker. Adjust solution pH to 7.
- Place the as-prepared titanate-CNT filter anode into the polycarbonate filtration casing and place another CNT-alone filter as cathode. Seal the casing.
- Pass through the filtration system with Sb(III) solution at a given flow. Apply a DC voltage during filtration.
- Determine the Sbtotal and Sb(III) concentration with atomic fluorescence spectrometer technique17.
NOTE: In this process, flow rate and applied voltage can be tuned by a peristaltic pump and a DC power supply, respectively.
Representative Results
The electroactive filtration apparatus employed is an electrochemically modified polycarbonate filtration casing (Figure 1). Field emission scanning electron microscope (FESEM) and transmission electron microscopy (TEM) techniques are employed to characterize the morphology of the titanate-CNT filter (Figure 2). To demonstrate the efficacy of the electrochemical filtration system, the change of Sbtotal and Sb valence state as a function of time is determined (Figure 3).
The FESEM images of titanate-CNT filter suggest a roughened surface. TEM characterization suggests that these CNTs are entangled with titanate nanowires. This suggests that we have successfully synthesized the titanate-CNT hybrid materials (Figure 2).
The change of Sbtotal and Sb valence state as a function of time at 2 V are examined (Figure 3). Results suggest that the Sb(V) concentration rises sharply within the initial 0.5 h and complete Sb(III) conversion is observed over 1 h continuous filtration in the recirculation mode. This indicates that Sb(III) oxidation is the main reaction process in the initial stage, then the Sb(V) can be adsorbed effectively by the loaded titanate nanowires. Furthermore, both Sb sorption kinetics and capacity increased with applied voltage due to enhanced electrostatic interactions and near surface transport by electromigration.
Figure 1: Electroactive filtration apparatus. (1) is the anodic titanium ring connector to the anodic filter, (2) is the titanate-CNT anodic filter, (3) is the insulating seal, (4) is the cathodic CNT filter, and (5) is the titanium ring connector to the cathodic filter. Please click here to view a larger version of this figure.
Figure 2: (A) FESEM and (B) TEM characterizations of the titanate-CNT filter. This figure has been modified from ref 19. Copyright 2019 Elsevier. Please click here to view a larger version of this figure.
Figure 3: Changes of Sb species as a function of time. Experimental conditions. E = 2 V, [Sb(III)]0 = 800 μg/L, flow rate = 3 mL/min, pH0 = 7 and 1 mM Na2SO4 electrolyte19. This figure has been modified from ref 19. Copyright 2019 Elsevier. Please click here to view a larger version of this figure.
Discussion
The key to this technology is to fabricate an electroactive conductive and porous hybrid filter with high Sb-specificity. To do this, special care should be paid to the fabrication process. The amount of titanate nanowires need to be precisely controlled due to the “trade-off” effect between the filter’s electrical conductivity and surface area.
In addition, it should be also noted that a proper applied voltage is necessary. Once the applied voltage is too high (e.g., >3 V), other competitive reactions, such as water splitting, may lead to the production of lot of bubbles (O2 at the anode and H2 at the cathode) at the electrode surface, which may block the active sites and, hence, contribute negatively to the Sb(III) removal performance.
The system stability in the long-term run is another issue of concern, since the accumulation of Sb-species on the filter’s surface is inevitable. This requires periodically wash of the filter to regenerate the active surface sites (especially chemical wash).
Meanwhile, the cost of this electroactive titanite-CNT filter still needs to be considered. Although the price of CNTs has significantly decreased due to the progress of their production technology in the past decades, their prices are still far higher than that of activated carbon and other carbon materials that are widely used.
Furthermore, it is noteworthy that the current experimental results are mainly obtained from a laboratory-scale electrochemical filtration device. Further scaling up the device to enable practical large-scale environmental applications will be the focus of our subsequent study.
We have developed a continuous-flow filtration system for simultaneous Sb(III) adsorption and sequestration. The key to this technology is an electroactive titanite-CNT filter featured with electrochemical reactivity, small pore size, readily available active sites, and high Sb specificity. This study provides new insights for the rational design of flow-through systems towards the decontamination of Sb and other similar heavy metal ions.
Açıklamalar
The authors have nothing to disclose.
Acknowledgements
This work was supported by the Natural Science Foundation of Shanghai, China (No. 18ZR1401000), the Shanghai Pujiang Program (No. 18PJ1400400), and the National Key Research and Development Program of China (No. 2018YFF0215703).
Materials
| Atomic fluorescence spectrometer | Ruili Co., Ltd | ||
| Carbon nanotubes (CNT) | TimesNano Co., Ltd | ||
| DC power supply | Dahua Co., Ltd | ||
| Ethanol, 96% | Sinopharm | ||
| Hydrochloric acid, 36% | Sinopharm | Corrosive | |
| L-antimony potassium tartrate | Sigma-Aldrich | Highly toxic | |
| N-methyl-2-pyrrolidinone (NMP), 99.5% | Sinopharm | Highly toxic | |
| Potassium hydroxide, 85% | Sinopharm | Corrosive | |
| Peristaltic pump | Ismatec Co., Ltd | ||
| Titanium dioxide powders | Sinopharm |
Referanslar
- Sun, W. M., et al. Profiling microbial community in a watershed heavily contaminated by an active antimony (Sb) mine in Southwest China. Science of the Total Environment. 550, 297-308 (2016).
- Herath, I., Vithanage, M., Bundschuh, J. Antimony as a global dilemma: geochemistry, mobility, fate and transport. Environmental Pollution. 223, 545-559 (2017).
- Pan, L. B., et al. Assessments of levels, potential ecological risk, and human health risk of heavy metals in the soils from a typical county in Shanxi Province, China. Environmental Science and Pollution Research. 23, 19330-19340 (2016).
- Huang, S. S., et al. Sulfide-modified zerovalent iron for enhanced antimonite sequestration: characterization, performance, and reaction mechanisms. Chemical Engineering Journal. 338, 539-547 (2018).
- Ungureanu, G., Santos, S., Boaventura, R., Botelho, C. Arsenic and antimony in water and wastewater: Overview of removal techniques with special reference to latest advances in adsorption. Journal of Environmental Management. 151, 326-342 (2015).
- Zou, J. P., et al. Three-dimensional reduced graphene oxide coupled with Mn3O4 for highly efficient removal of Sb(III) and Sb(V) from water. Acs Applied Materials & Interfaces. 8, 18140-18149 (2016).
- Saleh, T. A., Sari, A., Tuzen, M. Effective adsorption of antimony(III) from aqueous solutions by polyamide-graphene composite as a novel adsorbent. Chemical Engineering Journal. 307, 230-238 (2017).
- Yan, Y. Z., An, Q. D., Xiao, Z. Y., Zheng, W., Zhai, S. G. Flexible core-shell/bead-like alginate@PEI with exceptional adsorption capacity, recycling performance toward batch and column sorption of Cr(VI). Chemical Engineering Journal. 313, 475-486 (2017).
- Fu, L., Shozugawa, K., Matsuo, M. Oxidation of antimony (III) in soil by manganese (IV) oxide using X-ray absorption fine structure. Journal of Environmental Sciences. 73, 31-37 (2018).
- Liu, W., et al. Adsorption of Pb2+, Cd2+, Cu2+ and Cr3+ onto titanate nanotubes: competition and effect of inorganic ions. Science of the Total Environment. 456, 171-180 (2013).
- Wu, B., et al. Dynamic study of Cr(VI) removal performance and mechanism from water using multilayer material coated nanoscale zerovalent iron. Environmental Pollution. 240, 717-724 (2018).
- Shan, C., Ma, Z. Y., Tong, M. P. Efficient removal of trace antimony(III) through adsorption by hematite modified magnetic nanoparticles. Journal of Hazardous Materials. 268, 229-236 (2014).
- Luo, J. M., et al. Removal of antimonite (Sb(III)) and antimonate (Sb(V)) from aqueous solution using carbon nanofibers that are decorated with zirconium oxide (ZrO2). Environmental Science & Technology. 49, 11115-11124 (2015).
- Liu, Y. B., et al. Golden carbon nanotube membrane for continuous flow catalysis. Industrial & Engineering Chemistry Research. 56, 2999-3007 (2017).
- Ma, B. W., et al. Enhanced antimony(V) removal using synergistic effects of Fe hydrolytic flocs and ultrafiltration membrane with sludge discharge evaluation. Water Research. 121, 171-177 (2017).
- Yuan, Z. Y., Zhang, X. B., Su, B. L. Moderate hydrothermal synthesis of potassium titanate nanowires. Applied Physics a-Materials Science & Processing. 78, 1063-1066 (2004).
- Liu, Y. B., et al. Electroactive modified carbon nanotube filter for simultaneous detoxification and sequestration of Sb(III). Environmental Science & Technology. 53, 1527-1535 (2019).
- Gao, G., Vecitis, C. D. Electrochemical carbon nanotube filter oxidative performance as a function of surface chemistry. Environmental Science & Technology. 45, 9726-9734 (2011).
- Liu, Y. B., et al. Simultaneous oxidation and sorption of highly toxic Sb(III) using a dual-functional electroactive filter. Environmental Pollution. 251, 72-80 (2019).
